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PEER-REVIEWED ARTICLE bioresources.com
Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8451
Flammability Characteristics of Thermally Modified Oak Wood Treated with a Fire Retardant
Miroslav Gašparík,a,* Linda Makovická Osvaldová,b Hana Čekovská,a and
Dalibor Potůček a
Flammability characteristics were determined for oak wood (Quercus robur L.), which was thermally modified at 160, 180, and 210 °C. Subsequently, the thermally modified and unmodified wood was treated with a fire retardant. The effect of the thermal modification (TM) and fire retardant treatment (FRT) on the weight loss (WL), burning rate (BR), maximum burning rate (MBR), and time to reach the maximum burning rate (TRMBR) were evaluated. The FRT had an expected positive effect on all of the flammability characteristics, where the WL, BR, and MBR decreased, and the TRMBR increased. The TM temperature did not have a clear effect. As the TM temperature increased, the WL and BR decreased. The highest differences were found at 160 and 180 °C. As the TM temperature increased for the wood without the FRT, the TRMBR decreased. During the burning of the thermally modified wood with the FRT, the trend was the exact opposite.
Keywords: Burning rate; Maximum burning rate; Weight loss; Thermal modification; Fire retardant; Oak
Contact information: a: Department of Wood Processing, Czech University of Life Sciences in Prague,
Kamýcká 1176, Praha 6- Suchdol, 16521 Czech Republic; b: Department of Fire Engineering, Faculty of
Security Engineering, University of Žilina, Univerzitná 1, Žilina, 010 26 Slovakia;
* Corresponding author: [email protected]
INTRODUCTION
Wood is a natural material with many excellent properties (aesthetic and
mechanical) that make it suitable for versatile use. Despite those properties, wood has
certain disadvantages, such as a low resistance to biological agents (fungi, insects, etc.),
changes to the physical and mechanical properties, and high flammability. A common
method of protecting wood against most of these effects is thermal modification (TM).
TM is a newer type of wood modification. There are currently several types of
TM, the principle of which is different depending on the medium and temperature used
(Navi and Sandberg 2012). The most well-known types of TM are ThermoWood in
Finland, Plato Wood in the Netherlands, oil-heat treatment (OHT) in Germany, and Les
Bois Perdure and rétification process (Retiwood) in France (Esteves et al. 2011;
Sandberg and Kutnar 2016). In addition to these common TMs, there are also lesser
known TM processes that use superheated steam, such as Wood Treatment Technology
(WTT) in Denmark and Firmolin technology in the Netherlands, or a partial vacuum, like
Termovuoto in Italy (Ferrari et al. 2013). In general, TM can be defined as a process in
which high temperatures ranging between 150 and 260 °C are applied to wood in an
environment with different types of media (steam, nitrogen, oil, etc.) without chemical
substances (Sandberg and Kutnar 2016). TM remarkably affects the basic components of
wood. Cellulose and hemicellulose are polysaccharides found in the cell walls of wood.
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8452
Cellulose, which is responsible for the strength of wood fibers because of its high
polymerization degree, is more resistant to heat (Pandey 1999). Hemicellulose is less
resistant to heat, and its degradation leads to the most significant decrease in the
mechanical properties of thermally modified wood (Osvald and Gaff 2017). Lignin has
an aromatic structure and fills the spaces between the lignocellulosic fibers. It is
responsible for the rigidity of the material and is the most resistant to heat of these three
components (Cademartori et al. 2013). TM improves the dimensional stability, durability,
hygroscopicity, weather resistance, and resistance to fungi (Jämsä et al. 2000; Candelier
et al. 2013; Kačíková et al. 2013; Baysal et al. 2014; Kondratyeva et al. 2016). In
contrast, TM, especially above 220 °C, noticeably reduces the mechanical properties, e.g.
the modulus of rupture, hardness, and impact bending strength (Kamdem et al. 2002;
Kačík et al. 2015).
Mechanical properties are, however, only one group that is important for wood
products. Fire properties are also important because fire is one of the most critical
physical degradation factors for wood (Lee et al. 2004; Mohebby et al. 2007; Jiang et al.
2010). The fire properties of common wood-based materials have been thoroughly
explored. Although there are several studies that deal with the flammability and burning
of thermally modified wood (Martinka et al. 2013; Xing and Li 2014; Čekovská et al.
2017a; Čekovská et al. 2017b), their fire properties have only been investigated to a
limited extent. Thermally modified wood is susceptible to flames and burning
(Delichatsios et al. 2003), but is still used for interior and exterior elements. TM releases
volatile components from the wood and degrades lignin and polysaccharides, which are
closely related to the flammability and burning properties of wood (Manninen et al.
2002). Hence, thermally modified wood contains less volatile flammable components,
and the likelihood of it igniting and subsequently combusting is reduced (Martinka et al.
2013). The flammability of wood can be modified with fire retardants (Sogutlu et al.
2011; Lowden and Hull 2013).
Wood fire retardants affect the burning of wood by delaying the ignitability and
flame spread, and reducing the heat release (Östman et al. 2001; Hagen et al. 2009). Fire
retardants work on different principles, although most of them use several mechanisms at
once (Pries and Mai 2013). Most often, fire retardants create non-combustible charcoal
layers on the surface of the wood under the influence of temperature and physically
inhibit oxygen access to the wood (Jiang et al. 2014; Merk et al. 2015). Fire retardants
for wood use chemicals based on phosphorus, nitrogen, boron, and combinations of these
elements (Wang et al. 2004; Gao et al. 2006; Marney et al. 2008). Fire retardants are
applied through various methods. Vacuum pressure impregnation is highly effective
because it gets the fire retardant into a considerable depth, but it is only suitable for
structural elements, facing, and flooring materials before they are used. Soaking does not
require complicated machinery and is suitable for fire retardants that are in solutions that
can penetrate into wood. Coatings, which are suitable for existing structures and built-in
elements, use coating substances that form an insulating layer after they dry.
This research studied the flammability characteristics of thermally modified and
unmodified oak wood. Each group of samples was divided into two subgroups according
to their fire retardant modification. A two-component Flamgard Transparent coating was
used as the fire retardant. A burning test was used to evaluate the basic characteristics,
including the weight loss (WL), burning rate (BR), maximum burning rate (MBR), and
time to reach the maximum burning rate (TRMBR).
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EXPERIMENTAL Materials
Seventy-five-year-old pedunculate oak (Quercus robur L.), used in this study,
was harvested from the Poľana region in central Slovakia, near Zvolen. Wood samples
with the dimensions 20 × 100 × 200 mm were cut from the section located in the middle
distance between pith and bark (Fig. 1). The samples were divided into two groups: the
first group was thermally modified, while the second group was unmodified. Both groups
contained two subgroups, one of which consisted of fire retardant-treated samples, while
the other one contained samples that did not undergo the fire retardant treatment (FRT).
All of the samples were dried in a drying oven ULM 400 (Memmert GmbH & Co. KG,
Schwabach, Germany) at a temperature of 103 ± 2 °C until an oven-dry state was
reached. This condition facilitated the TM, and also induced similar moisture contents in
the samples without TM, which was important for comparison purposes.
Fig. 1. Oak samples
Procedures Thermal modification (TM)
The wood samples were modified in a thermal chamber (S400/03, LAC Ltd.,
Rajhrad, Czech Republic). Three final temperatures, 160, 180, and 210 °C, were chosen
for the wood modification. The TM used the ThermoWood principle developed by VTT
(Finland), which takes place in a protective atmosphere, dispersed water in the air, to
prevent overheating and burning. The TM of the wood was carried out in three basic
phases (Table 1).
Table 1. Conditions and Parameters of the Thermal Modification
Thermal Modification (TM) Temperature
160 °C 180 °C 210 °C
Heating 10.6 h 11.4 h 14.6 h
Thermal modification 3 h 3 h 3 h
Cooling 6.4 h 7.2 h 8 h
Total time 20 h 21.6 h 25.6 h
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8454
The first phase of the TM consisted of heating the wood. During this phase, the
temperature gradually increased until the desired temperature (160, 180, and 210 °C) was
reached. In the second phase, the final temperature was maintained for 3 h. This time was
the same for all of the TM temperatures. The third phase was characterized by a gradual
cooling. The temperature was gradually reduced to 40 °C so that the wood did not
undergo temperature and humidity shock when the chamber was opened. Then, the
samples rested for 3 h in the ambient environment. The densities of the samples are listed
in Table 2.
Table 2. Density and Moisture Content of the Oak Samples
Unmodified Thermal Modification (TM) Temperature
160 °C 180 °C 210 °C
Density before TM (kg/m3) 774 769 766 775
Density after TM (kg/m3) 774 736 683 673
Original moisture content (%) 10.5 10.8 10.7 11.2
Moisture content after TM (%) 5.5 5.8 4.9 4.2
Fire retardant treatment (FRT)
A two-component fire retardant coating from Flamgard Transparent (Stachema
a.s., Rovinka, Slovakia) was used. The first component is a foamable, water-soluble
coating substance (a mixture consisting of ammonium phosphates, a foam forming agent,
oxalic and acetic acid, and fire retardant additives) that was applied in three layers so that
the total spread was at least 500 g/m2. The second component is an acrylic cover lacquer
S 1818, which was applied in a single layer with a spread of at least 80 g/m2. Both
components were applied with a brush according to the conditions specified by the
manufacturer (Table 3). The curing of the individual layers took place at 20 °C.
Table 3. Properties and Application Conditions of the Fire Retardant Treatment
Component pH Density Thinner
Type
Wood Moisture Content
Content of Non-volatile Components
Application Ambient
Temperature
Hardening Time
Coating substance
2 to 3 1.2 g/cm3 hot water 10% min. 62% 10 to 35 °C 12 h/layer*
Cover lacquer
- 0.97 g/cm3 C 6000 - 31.5% 20 °C 4 h
* last layer must dry for 24 h
Methods Determination of the flammability characteristics
The flammability test was based on the direct application of flame to the wood,
according to ČSN 73 0862/B-2 (1991). In this study, the weight was measured
continuously during the test. Therefore, the sample holder and stand were placed on a
scale to measure the WL throughout the burning process (Fig. 2). A sample was placed in
the holder at a 45° angle to the horizontal plane with the assessed surface facing down.
The height of the propane burner flame was set to 10 cm. The burner was placed at the
center of the sample (intersection of the diagonals) so that the distance between the
mouth of the burner and center of the sample was 9 cm. Weight measurements were
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8455
taken at 10-s intervals using a laboratory scale (MS 1602S, Mettler Toledo, Greifensee,
Switzerland). The whole test lasted for 10 min (Fig. 3). In addition to the WL, the BR,
MBR, and TRMBR were also determined. Each combination of TM temperature and
FRT was represented by five samples according to ČSN 73 0862/B-2 (1991), so the
whole study contained 40 samples.
Fig. 2. Burning test apparatus
Fig. 3. Oak sample during the burning test
Evaluation and calculation
The effect of the factors on the flammability characteristics were assessed with
Statistica 13 software (Statsoft Inc., Tulsa, OK, USA) by analysis of variance (ANOVA).
The wood density was determined before and after the TM according to ISO
13061-2 (2014). The moisture content was determined according to ISO 13061-1 (2014).
Drying to an oven-dry state was also carried out according to ISO 13061-1 (2014).
The WL was calculated according to ČSN 73 0862/B-2 (1991) with Eq. 1,
1000
10
m
mmm (1)
where m is the WL (%), m0 is the weight of the sample before the test (g), and m1 is the
weight of the sample at a certain time interval (every 10 s as well as after 10 minutes) (g).
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8456
The burning rate was calculated with Eq. 2,
10010
0
10
t
tt
m
mmv (2)
where v is the burning rate (%/s), mt is the weight of the sample at time t (g), mt+10 is the
weight of sample 10 s later (g), and mt0 is the weight of sample at time 0 (g).
RESULTS AND DISCUSSION
The statistical evaluation of the effects from the factors and combination of
factors on the flammability characteristics of the oak wood are listed in Table 4.
Table 4. Effect of the Factors on the Flammability Characteristics
Monitored Factor Sum of Squares
Degrees of Freedom
Variance Fisher's F - Test
Significance Level P
Weight Loss
Intercept 3,246.213 1 3,246.213 1,045.588 0.000000*
Fire retardant treatment (FRT)
707.575 1 707.575 227.906 0.000000*
Thermal modification (TM) 110.173 3 36.724 11.829 0.000022*
FRT × TM 114.298 3 38.099 12.272 0.000017*
Error 99.350 32 3.105
Burning Rate
Intercept 3,995.002 1 3,995.002 129.1936 0.000000*
FRT 837.683 1 837.683 27.0896 0.000011*
TM 157.731 3 52.577 1.7003 0.186646
FRT × TM 318.824 3 106.275 3.4368 0.028347*
Error 989.523 32 30.923
Maximum Burning Rate
Intercept 44,906.75 1 44,906.75 518.4761 0.000000*
FRT 11,060.61 1 11,060.61 127.7016 0.000000*
TM 1,604.85 3 534.95 6.1763 0.001963*
FRT × TM 467.08 3 155.69 1.7976 0.167491
Error 2,771.62 32 86.61
Time to Reach the Maximum Burning Rate
Intercept 871,725.6 1 871,725.6 130.5345 0.000000*
FRT 20,475.6 1 20,475.6 3.0661 0.089524
TM 16,686.9 3 5,562.3 0.8329 0.485707
FRT × TM 31,036.9 3 10,345.6 1.5492 0.220857
Error 213,700.0 32 6,678.1
* Statistically significant (P < 0.05) factors or its combination
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Weight Loss The WL is a factor that directly represents the wood flammability, i.e. the greater
the WL of the wood, then the higher its flammability. A statistical evaluation of the effect
of the TM on the WL is shown in Fig. 4. On average, the WL of the thermally
unmodified wood was 7.5%. The thermally modified wood exhibited the highest WL of
11.6% at the lowest temperature of 160 °C, and the WL gradually decreased as the
temperature increased. The wood thermally modified at 210 °C had a WL identical to that
of the unmodified wood.
Fig. 4. Effect of the TM on the WL
The effect of the fire retardant (Fig. 5) was significant, and as was expected, the
WL was lower for the wood with the fire retardant coating. The fire retardant reduces the
burning capacity of wood, which logically suggests that the WL of the wood should be
lower. The wood without the FRT had an average WL of 13.2%, while the wood with the
FRT had a WL of only 4.8%, which was a decrease of 63.6%.
Fig. 5. Effect of the FRT on the WL
The interaction between the FRT and TM is shown in Fig. 6. The wood without
the FRT showed more pronounced differences in the WL values found for the treated
wood. The highest WL values for the wood without the FRT were found for the wood
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8458
modified at 160 and 180 °C. In this case, it is interesting to note that the average WL of
the unmodified wood was 9.9%, and for the wood thermally modified at 210 °C, it was
10.5%, which was a small difference.
Fig. 6. Effect of the TM and FRT on the WL
In the case of the wood with the FRT, smaller differences were observed at the
different TM temperatures. As with the previous case, the highest WL was measured at
160 °C, but the lowest WL was achieved with the wood thermally modified at 180 °C.
Burning Rate
The BR represents the spread of fire on a material over a certain time, i.e. a higher
BR means a better flammability of the material. In this study, the effect of the TM on the
BR was not clear (Fig. 7). The highest BR (13.2 × 10-5 %/s) was measured in the wood
thermally modified at 180 °C.
Fig. 7. Effect of the TM on the BR
In contrast, the unmodified wood achieved a 30.7% lower BR compared with the
wood thermally modified at 180 °C. The BR values of the wood thermally modified at
160 and 210 °C were almost the same. Čekovská et al. (2017a), who investigated the
effect of TM on the burning characteristics of spruce wood, found a similar effect from
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8459
the modification temperature on the BR.
The FRT (Fig. 8) had the same effect on the BR as it did on the WL, i.e. the wood
with the applied fire retardant had a lower BR (5.4 × 10-5 %/s) than that of the wood
without the FRT (14.6 × 10-5 %/s). The BR decreased by 63% because of the fire
retardant application. Fire retardants are specially designed to reduce burning, so this
effect on the BR was expected. The previous works by Marney et al. (2008), Lowden and
Hull (2013), and Jiang et al. (2014) confirmed this effect of fire retardants on various fire
characteristics of wood.
Fig. 8. Effect of the FRT on the BR
The thermally modified wood without the FRT exhibited great differences in
the BR at individual TM temperatures (Fig. 9). The highest BR was found at 180 °C,
while the lowest BR was found at 160 °C.
Fig. 9. Effect of the TM and FRT on the BR
The wood thermally modified at 210 °C achieved a BR similar to that found for
the unmodified wood. The FRT had a clear effect on the BR. After the application of the
FRT, these differences were reduced and the BR was dependent on the TM temperature,
i.e. the BR decreased as the modification temperature rose.
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8460
Maximum Burning Rate The dependence of the MBR on the TM temperature (Fig. 10) was very similar to
that found for the BR. A significant difference was evident in the wood thermally
modified at 160 °C, where the MBR values were the highest (44.3 × 10-5 %/s), which was
the opposite of the trend seen for the BR (Fig. 7). The MBR value for the wood thermally
modified at 180 °C was 9.5% higher than that of the wood thermally modified at 210 °C.
The MBR value of the wood thermally modified at 210 °C was close to the value
achieved for the unmodified wood, with a difference of only 1.7%.
Fig. 10. Effect of the TM on the MBR
In the case of the MBR, the FRT (Fig. 11) also had a significant effect on its
values. As for the previously discussed properties, the wood with the FRT achieved
significantly lower MBR values.
Fig. 11. Effect of the FRT on the MBR The FRT reduced the MBR by 66.3%, which was similar to the decrease seen for
the BR.
For the effects of the FRT and TM on the MBR (Fig. 12), there were differences
compared with the BR. The wood without the FRT reached the highest MBR values at a
TM temperature of 160 °C, which was the opposite of the trend observed for the BR (Fig.
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Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8461
9). For the wood with the FRT, the highest MBR value was achieved at a TM
temperature of 160 °C, and the lowest value was achieved at 180 °C.
Fig. 12. Effect of the TM and FRT on the MBR
Time to Reach the Maximum Burning Rate The TRMBR is a MBR-dependent factor, but has an opposite trend, i.e. the
higher the TRMBR, the slower the material burns. The TRMBR was strongly affected by
the TM temperature (Fig. 13). As the temperature increased, the TRMBR values
gradually decreased. The only significant change occurred at a TM temperature of 160
°C, where the TRMBR was significantly lower (120 s) compared with the other
temperatures.
Fig. 13. Effect of the TM on the TRMBR
As was expected, the FRT had a strong effect on the TRMBR (Fig. 14). The
higher the fire retardant ability, the higher the TRMBR. The wood treated with a fire
retardant achieved TRMBR values that were 26.6% higher than that of the untreated
wood.
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Fig. 14. Effect of the FRT on the TRMBR
Generally, the TRMBR was dependent on both the TM temperature and FRT
(Fig. 15 and Table 5). The application of a fire retardant caused the thermally modified
wood to achieve higher TRMBR values as the temperature increased for almost all of the
samples, except for the wood modified at 160 °C. In contrast, the wood without the FRT
showed the exact opposite behavior, i.e. as the TM temperature increased, the TRMBR
significantly decreased. The TRMBR for the wood without TM was 188 s, while the
wood thermally modified at 210 °C only reached 86 s, which was a decrease of 54.3%.
Čekovská et al. (2017a) found significantly smaller differences in the TRMBR values in
relation to the increase in the TM temperature for spruce wood.
Fig. 15. Effect of the TM and FRT on the TRMBR
The results in Table 5 show that in some cases there was a higher weight loss, but
the burning rate was the lowest. The relationship between BR and WL was not directly
proportional. WL represents the total loss of weight relative to the original weight of
sample, but does not describe how fast each proportion of wood was burnt over a 10-
second measuring interval. BR is influenced not only by the amount of the burnt mass of
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wood, but also by the proportion of its basic constituents found there. Higher proportion
of hemicelluloses mean faster burning, but lower weight loss. Conversely, a higher
proportion of cellulose and lignin means slower burning, but higher weight loss. These
proportions are also influenced by the thermal modification, which influences the various
components differently. Hemicellulose is the least resistant to temperatures and its
decomposition is up to 200 °C. Above this temperature, only cellulose and lignin remain,
but they burn more slowly than hemicellulose.
Table 5. Average Values of the Flammability Characteristics
Factors Flammability Characteristics
Fire Retardant Treatment
Thermal Modification
(°C)
Weight Loss (%)
Burning Rate
(× 10-5 %/s)
Maximum Burning
Rate (× 10-5 %/s)
Time to Reach Maximum
Burning Rate (s)
without FRT unmodified (reference)
9.9 (22.8) 13.2 (16.1) 41.7 (14.5) 188 (2.8)
without FRT 160 16.4 (16.3) 9.9 (14.8) 62.9 (3.5) 114 (7.8)
without FRT 180 16.0 (13.5) 22.4 (18.6) 52.9 (5.9) 112 (2.3)
without FRT 210 10.5 (10.7) 12.8 (6.9) 43.0 (1.5) 86 (17.6)
with FRT unmodified (reference)
5.1 (4.4) 7.1 (3.5) 16.8 (5.4) 160 (8.8)
with FRT 160 6.8 (4.7) 6.4 (3.3) 25.7 (2.3) 125 (3.6)
with FRT 180 2.6 (20.4) 3.9 (6.7) 10.6 (3.6) 204 (6.8)
with FRT 210 4.7 (12.5) 4.3 (6.2) 14.4 (3.9) 192 (4.8)
The values in parentheses are the coefficients of variation (CV, %).
Thermally modified wood has properties that have been changed, which affect its
ignition and subsequent burning behavior. The properties of thermally modified wood
depend not only on the wood species and its properties, but also on the modification
method and final temperature used during modification. Under high temperatures, the
three basic components of wood begin gradually decompose, which produces volatile
gases, tar, and carbonaceous char (Lowden and Hull 2013). However, each component
has a different resistance. TM up to 210 °C (the highest temperature in this study) affects
all of the basic wood components, but hemicellulose pyrolysis is the most pronounced
process because it begins at 180 °C (Kim et al. 2006). High temperatures cause the
degradation of cell wall polymers, which results in a reduction in volatile pyrolysis
products and reduces the flammability of the wood (Hirata et al. 1991; Kol and Sefil
2011). From this perspective, thermally modified wood should be more suitable in
regards to fire safety. In contrast, depending on the TM temperature, the surface integrity
of the thermally modified wood is disrupted to a certain extent, which leads to easier
ignition. The surface application of fire retardants is therefore suitable for thermally
modified wood.
In general, wood treated with fire retardants requires a higher temperature and
longer exposure to flames to burn. When the wood is exposed to flames, it releases
pyrolysis gases, which, however, contains less combustible gases needed for the wood to
burn (Hagen et al. 2009). Flame retardants based on phosphorus are the most common
fireproof chemicals for wood (Schartel 2010). Their advantage is that they directly affect
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the thermal degradation of wood. During wood pyrolysis, the phosphorus components
produce acids that reduce the decomposition temperature. This effect results in char
formation and the dehydration of wood components (George and Susott 1971; Stevens et
al. 2006). With this char layer on the surface, wood can resist further flame exposure
because this layer increases the thermal resistance between the underlying wood and
pyrolysis. The result is a reduction in the heat release rate and creation of a barrier against
the release of volatiles from the wood and their subsequent mixing with oxygen in the air
(Yang et al. 2003). Additionally, it is assumed that phosphorus prevents the formation of
flammable components (e.g. tar = levoglucosan) by the phosphorylation of cellulose.
The information available on the flammability and burning of thermally modified
wood with or without FRT is not extensive, and therefore it is important to study it
further.
CONCLUSIONS
1. The WL did not have a clear dependence on the TM temperature, whereas the FRT
had a clear effect. The highest WL values were found for the wood thermally
modified at 160 and 180 °C, which were 16.4% and 16%, respectively. However, the
WL observed in the wood thermally modified at 210 °C (9.9%) was comparable to
the WL measured for the unmodified wood (10.5%). The differences in the wood
with the FRT were much lower. As the TM temperature increased, the WL decreased,
except for the wood modified at 160 °C.
2. The BR of the thermally modified wood without the FRT had different values
depending on the TM temperature. The lowest BR was achieved at a TM temperature
of 160 °C, and the highest BR was found for the wood modified at 180 °C. The BR of
the wood modified at 210 °C was comparable to that of the unmodified wood. In
contrast, the FRT application on the thermally modified wood resulted in the
equalization of the differences and a gradual decrease in the BR of up to 38.1% as the
modification temperature increased.
3. The MBR of the thermally modified wood with or without FRT had a similar
dependence on the TM temperature, i.e. the highest MBR was found at a TM
temperature of 160 °C. As the TM temperature increased further, the MBR decreased.
The MBR values for the thermally modified wood ranged from 10.6 to 26.7 × 10-5
%/s, and for the thermally modified wood without the FRT, the MBR values ranged
from 41.7 to 62.9 × 10-5 %/s.
4. The TRMBR of the thermally modified wood without the FRT decreased
significantly as the TM temperature increased. The unmodified wood had an average
TRMBR value of 188 s, but when the temperature was 160, 180, and 210 °C, it
dropped to 114, 112, and 86 s, respectively. The FRT caused the TRMBR to increase
to 192 and 204 s for the wood modified at 180 and 210 °C, respectively. For the
modification at 160 °C, a decline in the TRMBR was observed.
PEER-REVIEWED ARTICLE bioresources.com
Gašparík et al. (2017). “Burning thermally mod. oak,” BioResources 12(4), 8451-8467. 8465
ACKNOWLEDGEMENTS
This research was supported by the University-wide Internal Grant Agency of the
Faculty of Forestry and Wood Science at the Czech University of Life Sciences Prague,
project CIGA 2016-4309.
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Article submitted: July 5, 2017; Peer review completed: September 10, 2017; Revised
version received: September 22, 2017; Accepted: September 23, 2017; Published:
September 26, 2017.
DOI: 10.15376/biores.12.4.8451-8467